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Indoor Air
Quality Problems In New Homes
CBS
Newsletter
Spring 1997
pg. 6
Indoor Air Quality in New Energy-Efficient
Houses
Figure 1:
Measurements of total volatile organic compounds in five new
houses in Pennsylvania, Michigan, and Florida and median
concentration in U.S. EPA study.
In 1993, the Indoor Environment Program began
investigating indoor air quality in new energy-efficient houses.
Five new houses have been included in the study, all in the eastern
U.S. Two had nearly identical floor plans and were part of a
demonstration project near Pittsburgh, PA; one was built
conventionally, while the other incorporated a number of
energy-efficient features. The conventional house was studied for
one year following construction, and the energy-efficient house was
sampled on three occasions over a two-year period. The other three
demonstration houses were in separate projects. One of these houses
was investigated over a period of four months following
construction. Ventilation rates ranged from 0.07 to 0.4 h-1
(air changes per hour) with a median value close to 0.2 h-1,
indicating that these houses have tighter envelopes than older
housing and that current building practices have improved building
tightness.
Concentrations of airborne organic contaminants
were measured in all of the houses. These measurements included
formaldehyde, individual volatile organic compounds (VOCs), and
total VOCs (TVOC). Since ventilation rate data were also collected,
source strengths were calculated with a mass-balance model. These
estimates of source strengths made it possible to compare the
magnitudes of the emission sources in houses with different volumes
and ventilation rates.
The concentrations of formaldehyde in all five
houses were generally about 0.05 ppm (0.06 mg/m3), or
lower, a level at which less than one percent of the population is
expected to experience sensory irritation. The major sources of
formaldehyde in houses are primarily particle board underlayment for
floors and particle and fiberboard used for cabinetry and furniture.
In an early-1980s study of formaldehyde concentrations in new
energy-efficient houses, concentrations of 0.2 ppm were common. In
the intervening years, composite-wood manufacturers have reduced the
formaldehyde emissions of their products in response to concerns
about the adverse health effects of this compound.
The concentrations of TVOC in the houses ranged
from 0.65 to 12 mg/m3; the median value was 2.4 mg/m3
(see Figure 1). A large probability-based study of existing
residences by the U.S. EPA found that the median concentration of
TVOC representative of a population of about 600,000 was 0.7 mg/m3.
Thus, the TVOC concentrations in the new houses were, with one
exception, elevated compared to typical values. Calculated
whole-house source strengths ranged from about 0.2 to 3 grams per
hour of contaminants. Interestingly, there was only about a factor
of two reduction in source strengths over the one- and two-year
study periods in the two Pittsburgh houses. If interior finish
materials such as paints and floor coverings are the dominant
sources, source strengths should decrease substantially over a
period of only a few months. Because of the magnitude and
persistence of the source strengths in the Pittsburgh houses, the
dominant source was probably not these finish materials but rather
some other element of the houses (see below).
The dominant classes of compounds detected in the
house air samples were terpene hydrocarbons, aromatic hydrocarbons,
ketones, and aldehydes. In the Pittsburgh houses, the most abundant
compounds were alpha-pinene, d-limonene, acetone, pentanal, hexanal,
heptanal, nonanal and acetic acid. The aldehydes are of particular
concern because they are irritants and produce unpleasant odors at
low concentrations. Hexanal, the aldehyde with the highest
concentrations and source strengths in the houses, ranged in
concentrations from 0.02 to 0.9 mg/m3. Thus,
concentrations of hexanal alone often significantly exceeded the
odor threshold of 0.06 mg/m3. In the Pittsburgh houses,
acetic acid also exceeded its odor threshold and probably accounted
for some of the detectable odor.
The sources of the VOC emissions in these new
houses are still under investigation through field and laboratory
studies. One possibility is that structural components consisting of
natural lumber, laminated lumber, plywood, and oriented strandboard
are the dominant sources. These wood products are the most logical
sources of terpene hydrocarbons, aldehydes, and acetic acid. Because
they are present in a house in large amounts, they may form a
sizable chemical reservoir that could be a source of contaminant
emissions over extended periods. These contaminants may be entering
the indoor air through walls, ceilings, and floors for duct work,
plumbing, and electrical systems.
As demonstrated by the paired Pittsburgh houses,
the problems of persistently elevated VOC concentrations and odors
are probably not unique to energy-efficient houses, but rather may
be relatively common in new houses built with current construction
materials and techniques. Further research should be able to
demonstrate ways to reduce emissions, thereby reducing
concentrations of VOC contaminants in houses, by modifying materials
and construction practices used for new houses, including those
built with specific energy-efficient features. This solution might
avoid the need for increased ventilation rates, which would diminish
the energy-efficiency and comfort benefits of houses with tightly
sealed envelopes.
--Alfred T. Hodgson

Alfred T. Hodgson
Indoor Environment Program
(510) 486-5301; (510) 486-6658 fax
This research is supported by DOE's Office of
Building Technologies, and State and Community Programs.
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